Environmental Sciences Group, Department of Chemistry and Chemical Engineering, Royal Military College of Canada, Kingston, ON K7K 7B4, Canada.
Environmental Sciences Group, Department of Chemistry and Chemical Engineering, Royal Military College of Canada, Kingston, ON K7K 7B4, Canada; Fipke Laboratory for Trace Element Research, University of British Columbia Okanagan, Kelowna, V1V 1V7, British Columbia, Canada.
Sci Total Environ. 2022 Feb 1;806(Pt 3):151248. doi: 10.1016/j.scitotenv.2021.151248. Epub 2021 Oct 29.
Silver nanomaterials (Ag NMs) have been used in a variety of commercial products to take advantage of their antimicrobial properties. However, there are concerns that these AgNMs can be released during/after use and enter wastewater streams, potentially impacting aquatic systems or accumulating in wastewater biosolids. Biosolids, which are a residual of wastewater treatment processes, have been found to contain AgNMs and are frequently used as agricultural fertilizer. Since the function of soil microbial communities is imperative to nutrient cycling and agricultural productivity, it is important to characterize and assess the effects that silver nanomaterials could have in agricultural soils. In this study agricultural soil was amended with pristine engineered (PVP-coated or uncoated AgNMs), aged silver (sulphidized or released from textiles) nanomaterials, and ionic silver to determine the fate and toxicity over the course of three months. Exposures were carried out at various environmentally relevant concentrations (1 and 10 mg Ag/kg soil) representing between 30 to over 800 years of equivalent biosolid loadings. Over thirteen different methodologies and measures were used throughout this study to assess for potential effects of the silver nanomaterials on soil, including microbial community composition, average well colour development (AWCD) and enzymatic activity. Overall, the AgNM exposures did not exhibit significant toxic effects to the soil microbial communities in terms of density, activity, function and diversity. However, the positive ionic silver treatment (100 mg Ag/kg soil) resulted in suppression to microbial activity while also resulting in significantly higher populations of Frankia alni (nitrogen-fixer) and Arenimonas malthae (phytopathogen) as compared to the negative control (p < 0.05, Tukey HSD) which warrants further investigation.
纳米银材料(Ag NMs)已经被广泛应用于各种商业产品中,以利用其抗菌性能。然而,人们担心这些 AgNMs 在使用过程中/之后可能会释放到废水中,并有可能对水生系统造成影响,或者在废水生物固体中积累。生物固体是废水处理过程的残余物,已经被发现含有 AgNMs,并且经常被用作农业肥料。由于土壤微生物群落的功能对养分循环和农业生产力至关重要,因此,表征和评估银纳米材料对农业土壤可能产生的影响非常重要。在这项研究中,原始工程(PVP 涂层或未涂层的 AgNMs)、老化银(硫化或从纺织品中释放)纳米材料和离子银被添加到农业土壤中,以确定在三个月的过程中它们的命运和毒性。暴露在不同的环境相关浓度下(1 和 10 mg Ag/kg 土壤),代表了 30 到 800 多年等效生物固体负荷。在这项研究中,使用了十多种不同的方法和措施来评估银纳米材料对土壤的潜在影响,包括微生物群落组成、平均好氧颜色发展(AWCD)和酶活性。总体而言,AgNM 暴露在土壤微生物群落的密度、活性、功能和多样性方面没有表现出显著的毒性效应。然而,阳性离子银处理(100 mg Ag/kg 土壤)导致微生物活性受到抑制,同时导致弗兰克氏菌(固氮菌)和 Arenimonas malthae(植物病原菌)的种群显著增加,与阴性对照相比(p<0.05,Tukey HSD),这值得进一步调查。